CN103787480A - Waste liquid treatment method of gram stain two-step method - Google Patents

Waste liquid treatment method of gram stain two-step method Download PDF

Info

Publication number
CN103787480A
CN103787480A CN201210418360.4A CN201210418360A CN103787480A CN 103787480 A CN103787480 A CN 103787480A CN 201210418360 A CN201210418360 A CN 201210418360A CN 103787480 A CN103787480 A CN 103787480A
Authority
CN
China
Prior art keywords
waste liquid
stain
trichloroisocyanuric acid
aqueous solution
counterstain
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201210418360.4A
Other languages
Chinese (zh)
Inventor
叶元康
徐燕萍
叶鸿
叶鹰
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
WUXI FAYE BIOSCIENCE Co Ltd
Original Assignee
WUXI FAYE BIOSCIENCE Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by WUXI FAYE BIOSCIENCE Co Ltd filed Critical WUXI FAYE BIOSCIENCE Co Ltd
Priority to CN201210418360.4A priority Critical patent/CN103787480A/en
Publication of CN103787480A publication Critical patent/CN103787480A/en
Pending legal-status Critical Current

Links

Abstract

The present invention discloses a waste liquid treatment method of a gram stain two-step method. The waste liquid treatment method comprises: adding a trichloroisocyanuric acid aqueous solution or a flaky trichloroisocyanuric acid solid to a collected primary stain and counter staining waste liquid to produce precipitate, and filtering, wherein the primary stain agent is a crystal violet-containing aqueous solution, the counter staining agent is an ethanol solution containing basic fuchsin, potassium iodide and iodine, a volume ratio of the waste liquid to the trichloroisocyanuric acid aqueous solution is 10:1-30:1, and the feeding amount of the flaky trichloroisocyanuric acid solid in per 100 mL of the waste liquid is 0.03-0.1 g. With the method, the waste liquid is effectively treated, such that the treated waste liquid achieves the waste water emission standard, and the environment pollution is reduced.

Description

A kind of method for treating waste liquid of gram stain two-step method
Technical field
The present invention relates to a kind of method for treating waste liquid, particularly relate to a kind of method for treating waste liquid of gram stain two-step method.
Background technology
Gram staining is widely used a kind of differential staining in bacteriology, within 1884, is founded by Denmark doctor Gram.Being differential staining very important in bacteriology, because dye by this method, can be gram positive organism (G+) and the large class of gram-negative bacteria (G-) two by discrimination of bacteria.Traditional gram staining method generally comprises just dyes, mordant dyeing, four steps such as decolours, redyes, wherein just stain is the ammonium oxalate crystal violet aqueous solution, mordant is the aqueous solution of iodine, counterstain is luxuriant red colouring liquid, traditional gram staining method is concentrated discharge after conventionally the waste liquid that contains dyestuff producing after dyeing being placed in to waste liquid cylinder, described waste liquid is not taked to effective treatment process, therefore environment causes larger pollution.
In order to simplify staining procedure, reduce the consumption of dyestuff, reduce environmental pollution, at present traditional gram's staining four step rule is also done to many improvement, wherein the most simple and effective is exactly to wash the gram stain two-step method of twice, the method mainly comprises just dyes and redyes two steps, and wherein said just stain is the aqueous solution that contains Viola crystallina, and described counterstain is the ethanolic soln that contains magenta, potassiumiodide, iodine.Although the method is by simplifying step compared with four step rule, reduce dye dosage, reduce to a certain extent the pollution of environment, the waste liquid that contains first stain and counterstain that the method is not mentioned producing carries out effective treatment process, therefore the waste liquid producing does not still reach standard that can safety dumping, and environment is equally easily caused to larger pollution.
Summary of the invention
The object of the invention is for there is no effective treatment process for the waste liquid producing in gram stain two-step method at present, easily cause the problem of environmental pollution, a kind of method for treating waste liquid of gram stain two-step method is provided, the method has carried out effectively processing for the rear waste liquid producing of dyeing, waste liquid after treatment is reached can emission standard, has reduced the pollution to environment.
Object of the present invention can be achieved through the following technical solutions:
A method for treating waste liquid for gram stain two-step method, comprises the following steps: in the waste liquid of the first stain of collecting and counterstain, add the trichloroisocyanuric acid aqueous solution or sheet trichloroisocyanuric acid solid, after generation precipitate, filter;
Wherein said just stain is the aqueous solution that contains Viola crystallina, described counterstain is the ethanolic soln that contains magenta, potassiumiodide, iodine, the volume ratio of described waste liquid and the trichloroisocyanuric acid aqueous solution is 10:1~30:1, described in every 100mL, in waste liquid, the charging capacity of sheet trichloroisocyanuric acid solid is 0.03g~0.1g.
Present method is by adding the trichloroisocyanuric acid aqueous solution or sheet trichloroisocyanuric acid solid in the waste liquid to containing the first stain that inclined and counterstain, after leaving standstill, filtering generation precipitate realizes, present method can make first stain and counterstain mixing stain and the trichloroisocyanuric acid generation complex compound in waste liquid and separate out, and makes sewage after treatment hospital sewage discharge up to standard national standard.
The present invention preferably, the trichloroisocyanuric acid that the described trichloroisocyanuric acid aqueous solution contains mass percent 1.0%~3.0%.
Preferably, the time of separating out of described precipitate is 5~24 hours in the present invention.
Preferably, in the described waste liquid that contains the first stain that inclined and counterstain, the volume ratio of first stain and counterstain is 1:2~3:0.8, more preferably 2:1 in the present invention.
The method for treating waste liquid of gram stain two-step method of the present invention has the following advantages:
In the waste liquid of present method by the first stain to containing collection and counterstain, add the trichloroisocyanuric acid aqueous solution or sheet trichloroisocyanuric acid solid, generation complex compound is separated out the step of rear filtration waste liquid has been carried out effectively processing, waste liquid after treatment has been reached can emission standard, has reduced the pollution to environment.
Embodiment
To the technical scheme in the embodiment of the present invention be clearly and completely described below, obviously, described embodiment is only the present invention's part embodiment, rather than whole embodiment.Based on the embodiment in the present invention, those of ordinary skills, not making the every other embodiment obtaining under creative work prerequisite, belong to the scope of protection of the invention.
In the present invention, use just stain, counterstain and trichloroisocyanuric acid to be conventional material, the filter method using in the present invention is the method for conventional use gauze and cotton filtration.
Embodiment 1
Collection contains in gram stain two-step method the first stain that inclined and the waste liquid 100ml of counterstain, wherein just stain is the aqueous solution that contains Viola crystallina, counterstain is the ethanolic soln that contains magenta, potassiumiodide, iodine, and the volume ratio of first stain and counterstain is 2:1; In described waste liquid, add the trichloroisocyanuric acid aqueous solution 10ml that contains mass percent 1.0%, leave standstill after 5 hours, generate complex compound and separate out, filter, water sample after treatment reaches the emission standard of quality examination unit.
Embodiment 2
Collection contains in gram stain two-step method the first stain that inclined and the waste liquid 100ml of counterstain, wherein just stain is the aqueous solution that contains Viola crystallina, counterstain is the ethanolic soln that contains magenta, potassiumiodide, iodine, and the volume ratio of first stain and counterstain is 1:2; In described waste liquid, add the trichloroisocyanuric acid aqueous solution 3.3ml that contains mass percent 3.0%, leave standstill after 24 hours, generate complex compound and separate out, filter, water sample after treatment reaches the emission standard of quality examination unit.
Embodiment 3
Collection contains in gram stain two-step method the first stain that inclined and the waste liquid 100ml of counterstain, wherein just stain is the aqueous solution that contains Viola crystallina, counterstain is the ethanolic soln that contains magenta, potassiumiodide, iodine, and the volume ratio of first stain and counterstain is 3:0.8; In described waste liquid, add the trichloroisocyanuric acid aqueous solution 5ml that contains mass percent 2.0%, leave standstill after 24 hours, generate complex compound and separate out, filter, water sample after treatment reaches the emission standard of quality examination unit.
Embodiment 4
Collection contains in gram stain two-step method the first stain that inclined and the waste liquid 100ml of counterstain, wherein just stain is the aqueous solution that contains Viola crystallina, counterstain is the ethanolic soln that contains magenta, potassiumiodide, iodine, and the volume ratio of first stain and counterstain is 1:2; In described waste liquid, add 0.1g sheet trichloroisocyanuric acid solid, leave standstill after 5 hours, generate complex compound and separate out, filter, water sample after treatment reaches the emission standard of quality examination unit.
Embodiment 5
Collection contains in gram stain two-step method the first stain that inclined and the waste liquid 100ml of counterstain, wherein just stain is the aqueous solution that contains Viola crystallina, counterstain is the ethanolic soln that contains magenta, potassiumiodide, iodine, and the volume ratio of first stain and counterstain is 1:1; In described waste liquid, add 0.06g sheet trichloroisocyanuric acid solid, leave standstill after 24 hours, generate complex compound and separate out, filter, water sample after treatment reaches the emission standard of quality examination unit.
Embodiment 6
Collection contains in gram stain two-step method the first stain that inclined and the waste liquid 100ml of counterstain, wherein just stain is the aqueous solution that contains Viola crystallina, counterstain is the ethanolic soln that contains magenta, potassiumiodide, iodine, and the volume ratio of first stain and counterstain is 3:1; In described waste liquid, add 0.03g sheet trichloroisocyanuric acid solid, leave standstill after 24 hours, generate complex compound and separate out, filter, water sample after treatment reaches the emission standard of quality examination unit.
The above; only for the better embodiment of the present invention, but protection scope of the present invention do not limit to therewith, is anyly familiar with in technical scope that those skilled in the art disclose in the present invention; the variation that can expect easily or replacement, within all should being encompassed in protection scope of the present invention.

Claims (4)

1. a method for treating waste liquid for gram stain two-step method, comprises the following steps:
In the first stain inclining to quilt and the waste liquid of counterstain, add the trichloroisocyanuric acid aqueous solution or sheet trichloroisocyanuric acid solid, after generation precipitate, filter;
Wherein said just stain is the aqueous solution that contains Viola crystallina, described counterstain is the ethanolic soln that contains magenta, potassiumiodide, iodine, the volume ratio of described waste liquid and the trichloroisocyanuric acid aqueous solution is 10:1~30:1, described in every 100mL, in waste liquid, the charging capacity of sheet trichloroisocyanuric acid solid is 0.03g~0.1g.
2. the method for treating waste liquid of gram stain two-step method as claimed in claim 1, is characterized in that, the trichloroisocyanuric acid that the described trichloroisocyanuric acid aqueous solution contains mass percent 1.0%~3.0%.
3. the method for treating waste liquid of gram stain two-step method as claimed in claim 1, is characterized in that, the time of separating out of described precipitate is 5~24 hours.
4. the method for treating waste liquid of gram stain two-step method as claimed in claim 1, is characterized in that, in the described waste liquid that contains the first stain that inclined and counterstain, the volume ratio of first stain and counterstain is 1:2~3:0.8.
CN201210418360.4A 2012-10-26 2012-10-26 Waste liquid treatment method of gram stain two-step method Pending CN103787480A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201210418360.4A CN103787480A (en) 2012-10-26 2012-10-26 Waste liquid treatment method of gram stain two-step method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201210418360.4A CN103787480A (en) 2012-10-26 2012-10-26 Waste liquid treatment method of gram stain two-step method

Publications (1)

Publication Number Publication Date
CN103787480A true CN103787480A (en) 2014-05-14

Family

ID=50663605

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201210418360.4A Pending CN103787480A (en) 2012-10-26 2012-10-26 Waste liquid treatment method of gram stain two-step method

Country Status (1)

Country Link
CN (1) CN103787480A (en)

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56124490A (en) * 1980-03-06 1981-09-30 Nissan Chem Ind Ltd Purification of waste water in dyeing process
CN87102687A (en) * 1982-10-22 1988-10-26 克莱斯塔尔克莱公司Sa The method of water treatment and product
CN1623923A (en) * 2003-12-02 2005-06-08 中国科学院生态环境研究中心 Compound water treatment oxidation decolour agent
CN101293689A (en) * 2007-08-15 2008-10-29 王旗 Water treatment medicament

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56124490A (en) * 1980-03-06 1981-09-30 Nissan Chem Ind Ltd Purification of waste water in dyeing process
CN87102687A (en) * 1982-10-22 1988-10-26 克莱斯塔尔克莱公司Sa The method of water treatment and product
CN1623923A (en) * 2003-12-02 2005-06-08 中国科学院生态环境研究中心 Compound water treatment oxidation decolour agent
CN101293689A (en) * 2007-08-15 2008-10-29 王旗 Water treatment medicament

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
许静: ""氰尿酸及其氯代衍生物的合成与研究"", 《中国优秀硕士学位论文全文数据库》, 7 July 2003 (2003-07-07) *

Similar Documents

Publication Publication Date Title
CN104710038B (en) A kind of method utilizing cellulose base flocculant coagulation decoloration dyeing waste water
CN102745761B (en) Recovery and utilization method for dyeing residual liquid of reactive dye
CN103466731B (en) A kind of fiber base sewage decoloring scavenging material and preparation method thereof
CN101381178B (en) Printing and dyeing wastewater processing technique
CN101830996B (en) Method for separating and purifying blue algae polysaccharide
CN104445781B (en) A kind of administering method of fused ring compound waste water
CN104628215A (en) Environmentally friendly technology for treating printing and dyeing wastewater through contact oxidation process
CN202936237U (en) Waste flue gas cooperated printing and dyeing wastewater processing system
CN105417614A (en) Heavy metal removal agent for mariculture water
CN103951056A (en) Treatment device capable of intensifying degrading of wastewater containing azo dyes by microbial electric auxiliary system and water treatment method
CN101948220B (en) Method for treating printing and dyeing wastewater
CN104926033A (en) Efficient treatment method for printing and dyeing wastewater
CN103787480A (en) Waste liquid treatment method of gram stain two-step method
CN105905994A (en) Novel method of utilizing process of conversion between chemical energy and electric energy of printing and dyeing wastewater to treat same
CN101249415A (en) Barium based adsorption material and method of preparing the same
CN106882860A (en) A kind of preparation method of magnesia-starch Complex Flocculant
CN1876227A (en) Process for preparing cation sorbent and its application
CN102826721B (en) Method for treating wastewater being generated during vitamin C production
CN105329972A (en) Straw composite material preparation method
CN108545879A (en) A kind of weaving Bleaching and dyeing sewage processing unit
CN208717053U (en) A kind of weaving Bleaching and dyeing sewage processing unit
CN102115275B (en) Method for treating methyl orange in azo dye wastewater by utilizing titaniferous blast furnace slag
CN104016527A (en) Textile dyeing wastewater treatment method
CN101696068B (en) Enhancing ultrafiltration treatment method of wastewater containing methylene blue by surfactant
CN104445715A (en) Treatment method for removing high-concentration nickel-containing electroplating wastewater

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
AD01 Patent right deemed abandoned

Effective date of abandoning: 20161019

C20 Patent right or utility model deemed to be abandoned or is abandoned